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  • 8/11/2019 Analysis of Aluminium Oxide and Silicon Carbide Ceramic Materials

    1/8

    J O U R N A L

    OF

    A N A L Y TI CA L A T O M I C S P E C T R O M E T R Y , S E P T E M B E R 1994, V O L .

    9 1063

    Analysis of Aluminium Oxide and Silicon Carbide Ceramic Materials

    by Inductively Coupled Plasma Mass Spectrometry

    Invited Lecture

    J. A. C. Broekaert

    Universitat Dortmund, Fachbereich Chemie, 0-44227 Dortmund, Germany

    R. Brandt

    Max-Planck-lnstitut fur Metallforschung, Stuttgart, Laboratorium fur Reinststoffanalytik, Postfach 722652,

    0-44073 Dortmund, Germany

    F. Leis

    C.

    Pilger

    and

    D. Pollmann

    lnstitut fur Spektrochemie und angewandte Spektroskopie, Postfach 707352,D-44073, Germany

    P. Tschopel and G. Tolgt

    Max-Planck-lnstitut fur Metallforschung, Stuttgart, Laboratorium fur Reinststoffanalytik, Postfach 122652,

    0-44073 Dortmund, Germany

    The use of inductively coupled plasma mass spectrometry (ICP-MS) for trace element determinations in

    A1203 and Sic powders as well as in compact Sic ceramics, subsequent to grinding to a particle size of

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    J O U R N A L

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    ANALYTICAL A TOMIC SPECTROM ETRY, SEPTEMBER 1994, VOL. 9

    Elemental, Winsford, UK) , the instrumental d ata and working

    parameters for which are listed in Table 1. The analytical

    parameters used were as proposed for the instrument by the

    manu facturer. For th e direct analyses of the samples subsequent

    to dissolution, pneumatic nebulization with a concentric glass

    nebulizer (Meinhard Associates, Santa Ana, CA, USA) and

    also with a Babington-type nebulizer (V-groove nebulizer,

    Fisons Instruments, VG Elemental) positioned in a laboratory -

    made cooled spray ch am ber 7 was used. In the on-line matrix

    removal using complexation of the trace elements, adsorption

    of the hexamethylenedithiocarbonate (H M D C ) complexes on

    an RP18 column, solid-phase extraction and high-pressure

    nebulization of the effluent were applied. A high-pressure

    nebulization system (Fa. Knauer, Berlin, Germany), as devel-

    oped by Berndt, was used in conjunction with desolvation,

    including both water and a Peltier cooling.'

    A combined knocking-grinding machine with a pestle as

    well as

    a

    mor tar m ade of high-purity S i c (Elektroschmelzwerk,

    Kempten) was used for grinding the compact S i c granulate

    material. The mortar vessel was held in a steel enclosure

    (Fig. 1). With this device it was found th at S i c granules w ith

    grains of between 1 and 20 mm side lengths can be pulverized.

    Below this grain size the grinding action of the machine was

    not effective, as it seem ed that a certain size is required for the

    pressure to w ork o n the granules. Below this size S i c pieces

    were found not to be split.

    Samp les and Reagents

    Th e A1,0, powd ers analysed included AKP-20 (mean particle

    size 0.57 pm, as ind icated by the m anufacturer, Sum itomo,

    Japan) and AKP-30 [mean particle size measured by auto-

    mated electron p robe microanalysis (EP MA ) 0.35 and 0.43 pm,

    as indicated by the manufacturer, Sumitorno] as well as ME/03

    (mean particle size measured by auto ma ted EP M A 0.35 pm).

    The ME/03 is a powder which has been characterized

    previously in a round-robin organized by the Arbeitskreis:

    Refraktarwerkstoffe in the Chem iker Ausschul3 der Gesellschaft

    Deutscher M etallhiitten- un d Bergleute (G DM B). The particle

    size distribution of the powders was determined by both

    autom ated EP M A (for a description of the m ethod, see ref. 9)

    Table

    1

    Plus ICP-MS instrument

    Instrumental and working parameters for the PQ2 Turbo

    ~~

    Generator

    Nebulizers

    V-groove nebulizer

    Concentric glass nebulizer

    Spray chamber

    Peristaltic pump

    Interface

    Sampler

    Skimmer

    Power

    Gas flows

    Outer

    Intermediate

    Aerosol carrier

    Sample uptake rate

    Sampling depth

    Vacuum

    1st stage

    2nd stage

    Mass spectrometer

    Mass range

    Dwell time

    Detector

    Henry, 2.0 kW, 27.12 MHz

    Meinhard Associates

    Scott-type made of quartz

    Gilson Minipuls 3

    Ni, aperture 1.0 mm

    Ni, aperture 0.7 mm

    1.35kW forward

    10-15 W reflected

    14lmin-'

    0.9-1.5 min-'

    0.9- 1.1 min 3 bar*)

    0.75-1.1 ml min-'

    10-12 mm

    2.0-3.0 mbar

    -=1 x mbar

    2.0-3.0 x mbar

    10-141 u for A1,0,, 5-239 u

    for Sic

    Dual mode, 640

    ps,

    pulse

    counting mode, 320

    ps

    Analogue-pulse counting

    'L

    ortar

    Rotating

    vibrator

    i

    teel ho l de r

    Fig.

    1

    Grinding device for compact Sic

    and by laser stray radiation measurements (laser particle sizer,

    Analysette 22- Fritsch, Idar-Ob erstein, Ge rm any ). Reasonable

    agreement between the results was obtained, considering that

    deviations possibly can arise from differences in the ultrasonic

    treatment of the suspension being measured and artifacts from

    the nuclepore filter loading encountered in the case of

    EPM A (Fig. 2).

    The S i c samples analysed were A10 (mean particle size

    xl pm, as indicated by the manufacturer, H.C. Starck,

    Gos lar, Germany) an d S-933 (Elektroschmelzwerk, Kem pten,

    Germany) in the form of a powder (mean part ic le s ize ~ 0 . 8m,

    as indicated by the manufacturer) and granules (grain size

    -10

    mm).

    The HC l and the

    H2S0,

    used for the sam ple decomposition

    were purified by sub-boiling distillation. All dilutions were

    20

    100

    80

    40

    20

    0

    b) 0.1 oF o 2.0

    /

    20

    10

    B

    0

    0 5 1

    5 10

    D

    a

    m

    ete

    r/pm

    Fig. 2 Particle size distribution obtained for the A1,0, powder

    AKP-30 (Sumitomo, Japan) by:

    a)

    EPMA (mean diameter= 0.35 pm);

    and b) aser light scattering (mean diameter=0.59 pm)

    1bar= 1 x lo5 Pa.

    View Article Online

    http://dx.doi.org/10.1039/ja9940901063
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    J O U R N A L OF ANALYTICAL AT OM IC SPECTRO METRY , SEPTEMBE R 1994, VOL. 9

    made with H 2 0 doubly distilled in qu artz equipment. The H F

    used (Merck, Darm stadt, Germany) was of Suprap ur quality.

    For the preparation of the standard solutions the respective

    Titrisol stock solutions (Merck) were used. Sample decompo-

    sitions were performed at high temperature and pressure in

    closed poly( tetrafluoroethylene) (P T F E ) vessels (Berghof DAB

    111, Tubing en, Ger ma ny) . In the m atrix removal studies,

    HMDC (Merck) and C,, RP18 columns (Fa. Knauer) were

    used.

    Results

    and

    Discussion

    Analysis

    ofA1203

    Powders

    After initial tests with an AlCl, solution, it was found th at the

    analyte solution for ICP-MS investigations should not contain

    more than ~ 2 0 0g ml of Al, which corresponds to a concen-

    tration of 400 pg ml-' of A1,0,. Indeed, at higher concen-

    trations high ablation of the sampler was observed and also a

    glassy deposit was soon formed on the skimmer. Both lead to

    clogging as well as to a deterioration of the short-term

    precision, expressed by the relative stan dard deviations (RSDs)

    and long-term drifts.

    15

    A

    t

    0 50

    100

    150

    200 250

    Time/min

    Fig .3 Long-term stability in ICP-MS analyses of A1203 after acid

    decomposition: A, 24Mg;B, 66Zn;C, '39La; D,139La:'I5In and E, 24Mg:

    45Sc. Sample solutions: 10ng ml-' of

    B,

    Na, Mg, Ti, V, Cr, Mn, Co,

    Ni,

    Zn, Ga, Zr, Ba, La and Ce;

    400

    pg ml- of A1203,

    10

    ng ml-' In

    and 50 ng ml-' of Sc in 0.04 moll- HC1-0.0064 moll- ' H 2 S 0 4 .

    ICP-MS:

    PQ2

    Turbo Plus with quartz spray-chamber

    (10

    C)

    (measurement conditions as in Table 1 . Measurement cycle: pre-flow,

    90 s; measurement time, 5

    x 60

    s; rinsing with acid solution,

    2.5

    min

    1065

    At a sample concentration of 4 0 0 p g m l - ' of A120,, the

    RSD s were 2-5% for impurity concen trations of 10 ng ml -'

    a n d in a 0.0 4m o 11 -1 H C1 a nd 6 . 4 ~op3m o l l - ' H 2 S 0 4

    solution, which are the concentrations of acid present after

    acid decomposition of the samples. However, when adding

    10

    ng ml -' of In an d 50 ng ml -' of Sc as internal stand ards ,

    the short-term precision for all elements investigated (B, Na,

    Mg, Ti, V, Cr, Mn, Co, Ni, Zn, Ga, Zr, Ba, La and Ce)

    becomes

    of

    the orde r of 1-2% an d drifts [with an intermediate

    washing stage of 2.5 min after each sam ple (measurement cycle:

    pre-flow 90 s, integration 5 x 60

    s)]

    after an initial period are

    below 5% over a period of 4 h (Fig. 3).

    For dissolution of the Al,O, powders treatment w ith HC1

    and H,SO, at 225C according to the following procedure

    was found to be optimum. A 1+0.001 g sample of A120,

    powder was transferred into a 150 ml PT FE vessel (Fa.

    Berghof) and 10ml of sub-boiled HCl plus 1 ml of sub-boiled

    H,SO, and 5m l of H 2 0 were also added. The mixture was

    allowed to react for 6 h at 225 C in the closed vessel. The

    resulting solution had been diluted 1

    +

    2500. Four solutions

    with matched acid concentrations and analyte concentrations

    of 0.4, 4, 40 and 400 ng ml -' and containing 5 ng ml -l of Rh

    as an internal standard were used for calibration purposes.

    The rinsing solution used contained 4m l

    of

    sub-boiled HCl

    and 0.4 ml

    of

    sub-boiled

    H , S 0 4

    in 1 1 of H,O.

    For analyte concen trations of 400 pg m l-' of A1203 , the

    detection limits obtained for ICP-MS (based on the 3s cri-

    terion), with a non-cooled spray chamber and considering the

    blank limitations of all reagents used, are listed in Table2.

    They range from 0.1 to

    4

    pg g- ' and a re higher for the low

    mass elements. However, severe blanks (N a) or sp ectral inter-

    ferences (Ca, Fe and Zn) are seen to occur. In the case

    of

    the

    instrument used, no systematic differences could be noticed

    when comparing the detection limits obtained in the scanning

    mode with those of the peak jumping mode for a dwell time

    of 640ps per channel and 25 scan cycles. Furthermore, the

    increased values found for a number of elements were clearly

    due to spectral interferences by oxygen, chlorine or sulfur

    containing cluster ions of argon (see Table

    3).

    Under the

    conditions originally used, the detection limits with ICP-MS

    for a number of elements with respect to the solid samples

    were even lower than with ICP-AES, however, only for

    elements with a mass below 60. At higher m asses this situation

    changes, as, with IC P-AE S, it is no longer possible to determine

    elements of interest in the concentration range required for the

    analysis of advanced ceramics.

    Table 2 Detection limits cL)

    (3s

    concept) of ICP-MS and ICP-AES for the analysis of A1203. Values in parentheses are for analyte solutions in

    distilled H20. Other values based on four replicates (ICP-MS)

    or

    12 replicates (ICP-AES)

    of

    the decomposition with all acids

    ICP-MS*

    Scanning mode,

    c,/ng ml

    -

    1.0

    (0.25)

    6.5 (0.4)

    2.0 (1.9)

    32 (6.4)

    0.8 (0.4)

    0.3 (0.1)

    36 (4.3)

    0.3 (0.07)

    2.0 (0.4)

    0.6 (1.4)

    0.06 (0.03)

    0.05 (0.04)

    (0.01)

    (0.02)

    0.01 (0.01)

    0.01)

    Peak jumping

    c,/ng ml-'

    1.3 (0.1)

    8.3 (1.3)

    1.4 (1.4)

    30 (3.8)

    1.4 (0.1)

    0.3 (0.06)

    35 (2.6)

    0.08

    (0.06)

    0.5

    (0.07)

    0.07 (0.07)

    1.8

    (0.2)

    0.8 (1.1)

    0.13

    (0.07)

    0.16 (0.16)

    0.06 (0.05)

    0.07 (0.05)

    CLIPg g

    -

    3.2

    18.0

    3.5

    75

    3.5

    0.75

    0.75

    1.2

    0.18

    4.5

    1.5

    0.32

    0.32

    0.15

    0.17

    87

    Actual?

    c,,lClg

    g

    0.6

    1.1

    0.7

    1.2

    0.04

    0.024

    0.08

    0.04

    0.8

    0.008

    0.23

    0.002

    0.008

    0.008

    ICP-AES:

    C J P g

    3

    -

    0.6

    0.03

    0.05

    0.3

    0.8

    2.1

    0.9

    ~~~~~~~ ~ ~

    *

    Sample dilution 1 +2500; PQ2 Turbo Plus.

    7 Values obtained after cooling the quartz spray chamber down to

    10

    C.

    $

    From

    ref.

    3.

    Sample

    dilution

    +50; 2 kW ICP, 0.9 m Czerny-Turner monochromator.

    View Article Online

    http://dx.doi.org/10.1039/ja9940901063
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    J O U R N A L OF ANALYT1CA.L ATOM IC SPECTROM ETRY, SEPTEM BER 1994, VOL. 9

    Table 3

    with HCl-H2S04 in a PTFE vessel

    Spectral interferences in ICP-MS for Alz03. Decomposition

    Analyte

    44Ca

    47Ti

    48Ti

    51v

    Cr

    53Cr

    Mn

    56Fe

    Fe

    60Ni

    64Zn

    66Zn

    71Ga

    Interferen

    12~160160, 2 7 ~ 1 1 6 0 ~

    3 3 ~ 1 4 ~

    3 2 ~ 1 6 0

    35CPO

    3 7 ~ 1 1 6 0

    4 0 ~ ~ 1 6 0

    35C1160H, 0Ar12C, 6Ar160, 6 S 1 6 0

    40Ar'4NH

    40Ar160H

    Cones

    3 2 ~ 1 6 0 1 6 0

    34~160160,

    3 2 ~ 3 4 s

    36Ar35C1

    In the case of the AK P-3 0 powder, results in the 0.1-2 pg g-'

    range were obtained for B, Ti, Cr, Mn, Ni,

    Cu,

    Zr, Ba, La and

    Ce (Table 4). The results obtained in the peak jump ing mode

    agreed well with those of the scanning mode. Even with the

    semiquantitative programe, the results deviated by less than a

    factor of two w ith only a few exceptions. In the case

    of

    Fe and

    Ca, however, severe deviations were obtained, which could

    relate more to interference problems, as these are known

    already from the early literature o n IC P- M S (see for example,

    ref. lo), than to blank limitations. The accuracy of the IC P-M S

    results obtained was evaluated by performing analyses of the

    ME/03 powder, which has also been analysed extensively by

    other techniques (Table 5 ) . Excepted for Fe, reasonable agree-

    Table 4 Results for analysis of Al,03 powder (AKP-30) by ICP-MS.

    All concentrations are in

    pg

    g- he standard deviations from four

    replicate analyses; final dilution, 1

    +

    2500; and internal standard, Rh

    Anal yte

    l l B

    47Ti

    Cr

    Mn

    60Ni

    6 3 c u

    71Ga

    'OZr

    138Ba

    I3'La

    l4OCe

    Semiquantitative Scanning mode

    Peak jumping

    2.2 0.2 4.5 10 .6 4.8 f0 .3

    1.3f0.3

    0.15 f O l

    2.6

    _+

    0.2 1.3f0.15 1.0 .07

    1.1 fO.1 0.7 .15 0.25 .09

    1.5f0 .1 0.7 .05 1.1 f0 .04

    0.05 .02

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    JOUR NAL O F ANALYTICAL ATOM IC SPECTROM ETRY, SEPTEM BER 1994, VOL. 9

    1067

    Table

    6 Determination of the leachable and the non-leachable impurities in the A1,0, samples AKP-20 and AKP-30 by ICP-MS when leaching

    with

    2

    (v/v) HN03. Figures in parentheses are the standard deviations from four replicate analyses. The results given for the alternative

    methods are from acid decomposition of the sample without applying leaching with

    2

    HNO, (v/v)

    Concentration/pg g-

    '

    Analyte

    B

    Na

    Mg

    Ca

    Ti

    V

    Cr

    Mn

    Fe

    c o

    Ni

    c u

    Zn

    Ga

    Zr

    Ba

    La

    Ce

    A K P - 2 0 -

    A K P - 3 0 -

    B

    Na

    Mg

    Ca

    Ti

    V

    Cr

    Mn

    Fe

    c o

    Ni

    c u

    Zn

    Ga

    Zr

    Ba

    La

    Ce

    Leachable

    2.8 (0.05)

    2.8 (0.09)

    0.98 (0.007)

    0.07 (0.001)

    0.2 (0.003)

    0.15 (0.004)

    0.026 (0.0003)

    1.0

    (0.1)

    0.002 (0.00005)

    0.1 (0.002)

    0.55

    (0.005)

    0.33 (0.01)

    0.006

    (0.0003)

    0.015 (0.0003)

    0.046 (0.003)

    0.037 (0.0005)

    1.1 (0.02)

    0.1 (0.002)

    0.82 (0.02)

    1.8 (0.04)

    1.2 (0.3)

    1.02 (0.02)

    0.1 (0.001)

    0.1 (0.002)

    0.09 (0.002)

    0.017 (0.0005)

    0.8

    (0.1)

    0.002 (0.0003)

    0.07

    (0.001)

    0.62 (0.003)

    0.33 (0.002)

    0.01 (0.0005)

    0.015 (0.0003)

    0.22 (0.004)

    0.29 (0.005)

    0.11 (0.002)

    Non-leachable

    6.5